JPS6025581A - Disposal of hexavalent chromium-containing coating material - Google Patents

Disposal of hexavalent chromium-containing coating material

Info

Publication number
JPS6025581A
JPS6025581A JP58133795A JP13379583A JPS6025581A JP S6025581 A JPS6025581 A JP S6025581A JP 58133795 A JP58133795 A JP 58133795A JP 13379583 A JP13379583 A JP 13379583A JP S6025581 A JPS6025581 A JP S6025581A
Authority
JP
Japan
Prior art keywords
hexavalent chromium
slurry
coating material
chromium
added
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP58133795A
Other languages
Japanese (ja)
Inventor
Kinichi Obata
小畠 欣一
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Suzuki Motor Corp
Original Assignee
Suzuki Motor Corp
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Suzuki Motor Corp filed Critical Suzuki Motor Corp
Priority to JP58133795A priority Critical patent/JPS6025581A/en
Publication of JPS6025581A publication Critical patent/JPS6025581A/en
Pending legal-status Critical Current

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  • Processing Of Solid Wastes (AREA)

Abstract

PURPOSE:To enable hexavalent chromium contained in a coating material to be discarded or be recovered as a valuable substance, by reducing hexavalent chromium to harmless trivalent chromium. CONSTITUTION:A hexavelent chromium-containing material is incinerated in an incinerator by adding appropriate combustion aids thereto. Then, the incinerated ash of the coating material is placed in a reducing device, water is added thereto to form a slurry, and after acidifying the slurry by adding a pH-adjusting agent thereto, sodium hydrogen sulfite, ferrous sulfate or sodium sulfite is added thereto as a reducing agent, and the resultant mixture is agitated. After reduction is completed, the slurry is neutralized, and is dehydrated to form a dehydrated cake, which can be disposed of as a waste material for use in reclamation or the like.

Description

【発明の詳細な説明】 本発明は六価クロム含有塗料を無害化して廃棄処理する
方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for rendering hexavalent chromium-containing paint harmless and disposing of it.

従来、六価クロム含有塗料は、セメントやアスファルト
などの固化剤を添加して固化物として埋立または、海洋
投棄する方法力どくよって廃棄されていた。ところが上
記固化物は、経年変化により、また衝撃などにより上記
固化剤の破損、侵蝕を招き、六価クロムが溶出し、環境
を再汚染する恐れがある。また、上記固化、埋立、およ
び海洋投棄による廃棄方法は、多大の費用、設備を必要
とするなどの問題があった。
Conventionally, hexavalent chromium-containing paints have been disposed of by force by adding solidifying agents such as cement or asphalt and disposing of the solidified material in landfills or in the ocean. However, the solidified material may cause damage and erosion of the solidifying agent due to aging or impact, and hexavalent chromium may be eluted and re-contaminate the environment. Further, the above-mentioned disposal methods such as solidification, landfill, and ocean dumping have problems such as requiring a large amount of cost and equipment.

本発明は、上記問題を解決し、塗料中の六価クロムを三
価クロムに還元して無害化し、廃棄するか有価物として
回収することのできる方法を提供するもので、その要旨
は、六価クロム含有塗料を焼却処理したのち、還元剤を
用いて六価クロムを三価クロムに還元することを特徴と
する六価クロム含有塗料の廃棄方法にある。
The present invention solves the above problems and provides a method that can reduce hexavalent chromium in paint to trivalent chromium, render it harmless, and dispose of it or recover it as a valuable resource. A method for disposing of a hexavalent chromium-containing paint is characterized in that the hexavalent chromium-containing paint is incinerated and then the hexavalent chromium is reduced to trivalent chromium using a reducing agent.

上記焼却処理は、通常の焼却炉を用いて行2うことかで
きるが、必要ならば、適当な助燃剤を加えて燃焼を速や
かに行なうことができる。また燃焼排、ガスの排出路の
途中に集じん器を設け、排ガス中の六価クロム粉じんを
除去することもできる。
The above-mentioned incineration process can be carried out using a normal incinerator, but if necessary, a suitable combustion aid can be added to speed up the combustion. Further, a dust collector can be provided in the middle of the combustion exhaust and gas exhaust path to remove hexavalent chromium dust in the exhaust gas.

上記還元は、六価クロム含有塗料の焼却灰を還元用装置
に入れ、水を加えてスラリー状とし、PH調整剤を加え
て酸性としたのち、還元剤を投入して攪拌して行うこと
ができる。該還元用装置は、ドラム回転方式、ミキサー
、バッチ式などいずれの装置を用いてもよい。またPH
調整剤は、焼却灰スラリーのPH,還元剤が還元作用を
行うことのできるPH範囲などを考慮して適宜、その添
加量、種類を選ぶことができる。例え杜、重亜硫酸ソー
ダを還元剤として用いた場合は、硫酸を用いて、PH2
,5以下にすることが望ましい。
The above reduction can be carried out by putting the incineration ash of the hexavalent chromium-containing paint into a reduction device, adding water to make a slurry, adding a pH adjuster to make it acidic, and then adding a reducing agent and stirring. can. As the reduction device, any device such as a drum rotation type, a mixer, or a batch type may be used. Also PH
The amount and type of the adjusting agent to be added can be appropriately selected in consideration of the PH of the incinerated ash slurry, the PH range in which the reducing agent can perform the reducing action, and the like. For example, if sodium bisulfite is used as a reducing agent, sulfuric acid is used to reduce the pH
, 5 or less.

上記還元剤としては、重亜硫酸ソーダ、硫酸第一鉄、亜
硫酸ソーダなどを用いることができる。
As the reducing agent, sodium bisulfite, ferrous sulfate, sodium sulfite, etc. can be used.

還元反応が終了したのち、適当な中和剤、例えば消石灰
を添加して該スラリーを中和する。
After the reduction reaction is completed, the slurry is neutralized by adding a suitable neutralizing agent, such as slaked lime.

該中和剤の添加量、種類は、スラリーの量、PH等によ
り適宜、決定することができる。
The amount and type of neutralizing agent to be added can be appropriately determined depending on the amount of slurry, pH, etc.

次に、該スラリーを通常の方法に従って脱水し、脱水ケ
ー・キを形成し、これを埋立等の廃棄処理にすることが
できる。
The slurry is then dewatered according to conventional methods to form a dewatered cake, which can be disposed of, such as in a landfill.

、 なお、上記の水、PH調整剤、還元剤および焼却灰
の還元装置への投入の順序は、上述の順序に限られず、
最初に水を還元用装置に入れたのち、PH調整剤、還元
剤を投入して混合【7てから、焼却灰を投入するという
順序でも行うことができる。
Note that the order in which the water, PH adjuster, reducing agent, and incinerated ash are introduced into the reduction device is not limited to the above-mentioned order.
This can also be done in the following order: first put water into the reducing device, then add the PH adjuster and reducing agent, mix [7], and then add the incinerated ash.

また、還元反応の進行に伴なってガスが発生する場合は
、該還元用装置の適当な箇所にガス排出口を設け、ガス
を排出できるようにすることが望ましい。
Further, when gas is generated as the reduction reaction progresses, it is desirable to provide a gas outlet at an appropriate location in the reduction device to allow the gas to be discharged.

以上のように、本発明は、化学反応を利用するので、処
理時間が数時間で充分であり、処理に長時間を要する置
部化より有利である。また、処理に必要な設備も固型化
処理等忙比べて小規模なものでよく、埋立費用も少なく
てすみ、処理費用を安価なものにすることができる。
As described above, since the present invention utilizes a chemical reaction, a treatment time of several hours is sufficient, which is more advantageous than in-place treatment, which requires a long treatment time. In addition, the equipment required for treatment may be smaller than that required for solidification treatment, etc., and landfill costs can be reduced, making it possible to reduce treatment costs.

実施例1 廃棄六価クロム含有塗料を焼却処理して焼却灰80kg
を得た。この焼却灰の六価クロム溶出濃度は85ppm
であった。
Example 1 Waste hexavalent chromium-containing paint is incinerated to produce 80 kg of incinerated ash.
I got it. The hexavalent chromium elution concentration of this incineration ash is 85 ppm.
Met.

次に、ドラム回転式還元装置内に水を300を入れ、重
亜硫酸ソーダ5に9.硫酸9kgを加えて混合したのち
、上記焼却灰80kgを投入しドラムを回転させて攪拌
した。反応混合物のPHはZ5以下であった。反応の進
行につれて亜硫酸ガスが発生するので、これを還元装置
に設けたガス抜きパルプから放出した。さら忙約5時間
靜置後、消石灰乳8に9/201水を投入して中和した
Next, put 300 ml of water into the drum rotary reduction device, add 5 ml of sodium bisulfite to 9 ml of water. After adding and mixing 9 kg of sulfuric acid, 80 kg of the above incinerated ash was added and stirred by rotating the drum. The pH of the reaction mixture was below Z5. As the reaction progressed, sulfur dioxide gas was generated and was released from a degassing pulp provided in the reduction device. After standing still for about 5 hours, 9/201 water was added to slaked lime milk 8 to neutralize it.

処理後の焼却灰からの六価クロム溶出濃度を測定したと
ころ、Oppmであった。
The concentration of hexavalent chromium eluted from the incinerated ash after treatment was measured and found to be Oppm.

実施例2 廃棄六価クロム含有塗料を焼却処理して焼却灰64に9
を得た。この焼却灰の六価クロム溶出濃度はas pp
mであった。
Example 2 Waste hexavalent chromium-containing paint is incinerated and incinerated ash 64 to 9
I got it. The hexavalent chromium elution concentration of this incineration ash is as pp
It was m.

次に、ドラム回転式還元装置に水を200を入れ、重亜
硫酸ソーダ4ki9.硫酸7ゆを加えて混合したのち、
上記焼却灰を投入し、ドラムを回転させて攪拌した。反
応の進行忙つれて、亜硫酸ガスが発生するので、これを
還元装置に設けたガス抜きパルプから放出した。さらに
約5時間静置後、消石灰乳7kg/20を一水を投入し
て中和した。
Next, put 200 ml of water into the drum rotary reduction device, and add 4 ki 9 ml of bisulfite soda. After adding 7 ml of sulfuric acid and mixing,
The above incineration ash was added and stirred by rotating the drum. As the reaction progressed, sulfur dioxide gas was generated, which was released from a degassing pulp provided in the reduction device. After leaving the mixture still for about 5 hours, 7 kg/20 of slaked lime milk was added to one water to neutralize it.

処理後の焼却灰からの六価クロム溶出濃度を測定したと
ころ、Oppmであった。
The concentration of hexavalent chromium eluted from the incinerated ash after treatment was measured and found to be Oppm.

Claims (2)

【特許請求の範囲】[Claims] (1)六価クロム含有塗料を焼却処理したのち、還元剤
を用いて六価クロムを三価クロムに還元することを特徴
とする六価クロム含有塗料の廃棄方法
(1) A method for disposing of paint containing hexavalent chromium, which comprises incinerating the paint containing hexavalent chromium and then reducing the hexavalent chromium to trivalent chromium using a reducing agent.
(2)上記還元剤が重亜硫酸ソーダ、硫酸第一鉄。 亜硫酸ソーダである特許請求の範囲第1項に記載の方法
(2) The reducing agent is sodium bisulfite or ferrous sulfate. The method according to claim 1, wherein the sodium sulfite is sodium sulfite.
JP58133795A 1983-07-22 1983-07-22 Disposal of hexavalent chromium-containing coating material Pending JPS6025581A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP58133795A JPS6025581A (en) 1983-07-22 1983-07-22 Disposal of hexavalent chromium-containing coating material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP58133795A JPS6025581A (en) 1983-07-22 1983-07-22 Disposal of hexavalent chromium-containing coating material

Publications (1)

Publication Number Publication Date
JPS6025581A true JPS6025581A (en) 1985-02-08

Family

ID=15113195

Family Applications (1)

Application Number Title Priority Date Filing Date
JP58133795A Pending JPS6025581A (en) 1983-07-22 1983-07-22 Disposal of hexavalent chromium-containing coating material

Country Status (1)

Country Link
JP (1) JPS6025581A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63308170A (en) * 1987-06-09 1988-12-15 浜田 倶衛 Method for preventing collapse of gravestone, monument, etc.
JPH06166726A (en) * 1993-07-13 1994-06-14 Sanyo Chem Ind Ltd Production of water absorptive resin
ITVE20090034A1 (en) * 2009-07-09 2011-01-10 Veneta Depuratori E Affini S Ve D A Soc PROCEDURE FOR TREATING ASHES OBTAINED IN WASTE INCINERATION PLANTS.-

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53113266A (en) * 1977-03-14 1978-10-03 Sakai Chem Ind Co Ltd Direct reatment method for powdered substance containing chromium
JPS5457530A (en) * 1977-10-15 1979-05-09 Toshiba Corp Method of treating waste coating

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS53113266A (en) * 1977-03-14 1978-10-03 Sakai Chem Ind Co Ltd Direct reatment method for powdered substance containing chromium
JPS5457530A (en) * 1977-10-15 1979-05-09 Toshiba Corp Method of treating waste coating

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS63308170A (en) * 1987-06-09 1988-12-15 浜田 倶衛 Method for preventing collapse of gravestone, monument, etc.
JPH06166726A (en) * 1993-07-13 1994-06-14 Sanyo Chem Ind Ltd Production of water absorptive resin
ITVE20090034A1 (en) * 2009-07-09 2011-01-10 Veneta Depuratori E Affini S Ve D A Soc PROCEDURE FOR TREATING ASHES OBTAINED IN WASTE INCINERATION PLANTS.-

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